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ARCHIVED REPORTS_ANNUAL 2010 GROUNDWATER MONITORING AND SAMPLING REPORT
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ARCHIVED REPORTS_ANNUAL 2010 GROUNDWATER MONITORING AND SAMPLING REPORT
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Last modified
5/13/2020 2:36:11 PM
Creation date
5/13/2020 2:16:56 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
ANNUAL 2010 GROUNDWATER MONITORING AND SAMPLING REPORT
RECORD_ID
PR0505768
PE
2960
FACILITY_ID
FA0006988
FACILITY_NAME
ALDEN PARK CHEVRON
STREET_NUMBER
500
Direction
N
STREET_NAME
SEQUOIA
STREET_TYPE
AVE
City
TRACY
Zip
95376
APN
23416001
CURRENT_STATUS
01
SITE_LOCATION
500 N SEQUOIA AVE
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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' Mr.Lee Higgins—CEMC <br /> Annual 2010 Groundwater Monitoring and Sampling Report April 19,2010 <br /> Alden Park <br /> ' Page 5 of 7 <br /> GROUNDWATER ANALYTICAL RESULTS <br /> Groundwater samples collected on January 5 and 6, 2010, from MW-4, MW-7 through <br /> MW-12, and MW-14 were analyzed for the following constituents: <br /> • TPHd(C1d—C25), using U.S. Environmental Protection Agency (EPA) Method <br /> ' 8015B; and <br /> • PAHs using EPA Method 8270C with large-volume injection. <br /> ' The groundwater analytical results are summarized and compared with the numerical <br /> State Water Quality Objectives (WQOs) and the RWQCB Region 2 Environmental <br /> Screening Levels (ESLs) in Tables 2 and 3.4 Analytical results exceeding the most <br /> tconservative ESL and/or WQO are highlighted in Tables 2 and 3 in bold font. TPHd <br /> were present above the WQO and ESL in MW-7, which is consistent with previous <br /> sampling events. The PAHs benzo(a)pyrene, benzo(b)fluoranthene, <br /> ' benzo(k)fluoranthene, dibenz(a,h)anthracene, and indeno(1,2,3-cd)pyrene were detected <br /> in MW-8 in concentrations that exceeded the respective WQOs and/or ESLs. A copy of <br /> the laboratory analytical report and the data usability summary are provided as <br /> 1 Attachment C. See Attachment C for details regarding data qualifiers. <br /> QUARTERLY SPO EXTRACTION AND PRODUCT-THICKNESS <br /> MEASUREMENTS <br /> Vacuum extraction of SPO was performed quarterly throughout 2009 (April 22, July 16, <br /> and November 24, 2009) and during the first quarter of 2010 (January 7, 2010). <br /> Approximately 122.3 gallons of SPO were removed from wells MW-1, MW-3,MW-5, <br /> MW-6, MW-15, MW-16, MW-18, MW-20, and MW-21 during 2009; and a total of <br /> ' 40.07 gallons were removed during the first quarter of 2010. Approximately 926.80 <br /> gallons of SPO have been removed from the wells to date. <br /> SPO thickness ranged from 5.89 feet in MW-1 to 10.30 feet in MW-6 during the first <br /> quarter 2010 event. Oleophilic socks are currently in wells MW-5 and MW-21. See <br /> Table 4 for a summary of SPO thickness measured and cumulative volumes extracted. <br /> Copies of the field data sheets containing SPO measurements are included as Attachment <br /> 1 B. <br /> OLEOPHILIC SOCK REPLACEMENT <br /> 1 Oleophilic socks were installed in MW-5 and MW-21 in 2004 due to the presence of <br /> relatively low amounts of SPO. The socks were removed and inspected on January 7, <br /> 2010. Approximately 0.06 gallon of SPO was recovered from MW-5, and a replacement <br /> ' sock was installed. No measurable SPO was recovered from MW-21, and the sock was <br /> re-installed. <br /> 1 4. The WQOs are defined b the Porter-Cologne Act " <br /> Y g as the levels or limits of water quality constituents or <br /> characteristics which are established for the reasonable protection of beneficial uses of water or the prevention of <br /> ' nuisance within a specific area." The ESLs(provided as a reference)are a tool based on conservative standard <br /> exposure factors for initial human health and the environment screening-level evaluations of analytical results. <br />
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